Agriculture Reference
In-Depth Information
Table 11.1 Mediterranean-type climate regions and biogeographic characteristics
Mediterranean
Basin
California
Floristic Province Central Chile
Cape Floral
Region
Southwest
Australia
Original primary
vegetation (km 2 )
2 362 000
324 000
300 000
74 000
309 850
Remaining
vegetation (%)
4.7
24.7
30.0
24.3
10.8
Plant species
25 000
4426
3429
8200
5469
Endemics (%)
52
48
47
69
79
Dominant
shrublands
maquis/garrigue
chaparral
matorral
fynbos
heath
Fire-dependent
ephemeral flora
none
dominant
none
minor
minor
Geophytes
moderate
moderate
moderate
very
abundant
very
abundant
Annuals
abundant
abundant
abundant
minor
minor
Colonization from
outside burn
abundant
rare
none?
none
none
Shrubs resprouting most species
half of species most species
half of
species
half of
species
Shrubs with
fire-stimulated
seedling
recruitment
many species in a
few genera
many species in a
few genera
1 or a few
species
many
species,
many
genera
many
species,
many
genera
low in closed-
canopy
shrublands
higher in
open sites
generally
high
generally
high
Prefire diversity
low in closed
canopy; high in
disturbed sites
low in closed-
canopy
shrublands;
higher in open
sites
the relative change in vegetation structure after fire. Northern hemisphere MTC
ecosystems largely are dominated by moderately fertile soils and, in the absence of
recent disturbance, often develop closed-canopy shrublands and woodlands (see
Chapters 4 and 5 ). The dominant sclerophyllous-leaved species typically form a
monolayer of tall (2-5 m) evergreen shrubs that shade out most understory
species. Consequently community diversity tends to be rather low, comprising
mostly shrubs and a few vines and lianas. In the understory there may be sparse
populations of a few annual and herbaceous perennial species but these popula-
tions fluctuate with annual precipitation and often disappear under drought
conditions. In the soil, however, there is a rich diversity of long-lived dormant
seeds, bulbs and corms that are triggered to germinate and resprout in response to
fire. As a consequence these communities exhibit dramatic increases in diversity
after fire ( Table 11.2 ).
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